Literature DB >> 27698584

Melicope oppenheimeri, section Pelea (Rutaceae), a new species from West Maui, Hawaiian Islands: with notes on its ecology, conservation, and phylogenetic placement.

Kennetah R Wood1, Marc S Appelhans2, Warren L Wagner3.   

Abstract

Melicope oppenheimeri K.R. Wood, Appelhans & W.L. Wagner (section Pelea (A. Gray) Hook. f., Rutaceae), a rare endemic tree from West Maui, Hawaiian Islands, is described and illustrated with notes on its ecology, conservation, and phylogenetic placement. The new species differs from Hawaiian congeners by its carpels basally connate 1/5, narrowed into a strongly reflexed beak 10-15 mm long. It also differs in a combination of leaves with 7-10 pair of secondary veins; cymes to 3 cm long; peduncles 5-6.5 mm long; flowers perfect; capsules 4-9 × 40-52 mm; and a densely appressed short-sericeous ovary. Melicope oppenheimeri is known only from an isolated cliff-base plateau in upper Waihe'e Valley, West Maui. Its discovery brings the number of recognized Melicope J.R. Forst. & G. Forst. species in the Hawaiian Islands to 49. A table is included indicating the conservation status of Hawaiian Melicope and Platydesma H. Mann., which is nested within Melicope sect. Pelea. Melicope oppenheimeri falls into the IUCN Critically Endangered (CR) Red List category.

Entities:  

Keywords:  Critically Endangered; Hawaiian Islands; Melicope; Melicope section Pelea; Rutaceae; West Maui; new species

Year:  2016        PMID: 27698584      PMCID: PMC5029140          DOI: 10.3897/phytokeys.69.8844

Source DB:  PubMed          Journal:  PhytoKeys        ISSN: 1314-2003            Impact factor:   1.635


Introduction

J.R. Forst. & G. Forst. is the largest genus of the family () and consists of ca. 235 species of shrubs and trees (Hartley 2001, Appelhans et al. 2014a). The distribution of ranges from the Malagasy and Indo-Himalayan regions in the east to the Hawaiian and Marquesan Islands in the west and from Nepal, southern China, Taiwan and the Japanese Ogasawara Islands in the north to New Zealand and Australia in the south (Hartley 2001). Ongoing phylogenetic studies of and closely related genera indicate the need for revisionary work in this group with several of the related small genera belonging in in order for it to be monophyletic (Harbaugh et al. 2009, Appelhans et al. 2014b). In the most recent systematic revision by Hartley (2001) was subdivided into four sections: (Lour.) T.G. Hartley; ; (A. Gray) Hook. f.; and T.G. Hartley. Only proved to be a monophyletic group in a recent molecular study (Appelhans et al. 2014b). The currently known 48 endemic Hawaiian species are all members of , which consists of 85 species almost exclusively restricted to the Australasian–Outer Melanesian–Pacific region. Within , only the Hawaiian group proved to be monophyletic (Appelhans et al. 2014c). The Hawaiian endemic species all have unifoliolate leaves; plants presumably hermaphroditic or dioecious; carpels that range from being basally connate to fully connate, and with variations in exocarp and endocarp that contrast from glabrous to pubescent. Hartley (2001) inferred that was present in eastern Gondwanaland before about 96 Ma and states that the Hawaiian species represent a radiation that most likely traces back to a single colonization of the archipelago by a species from . While Hartley’s age estimate of is doubtful since the oldest fossils of the whole family date to the Late Cretaceous (Knobloch and Mai 1986, Gregor 1989) and molecular dating studies estimated its origin in the Oligocene or Miocene (Muellner et al. 2007, Appelhans et al. 2012), his suggestion for a single colonization of the Hawaiian archipelago was supported by molecular phylogenetic analyses (Harbaugh et al. 2009, Appelhans et al. 2014b, c). The most recent molecular phylogenetic studies also indicate that the Hawaiian genus H. Mann is nested within and that the seven known Marquesan endemics are a closely related group resultant from two independent colonization events from Hawaiian (Harbaugh et al. 2009, Appelhans et al. 2014c).

Methods

All measurements and descriptions were taken from dried herbarium specimens or from notes made in the field and are presented in the descriptions as follows: length × width, followed by units of measurement (mm or cm).

Taxonomic treatment

K.R. Wood, Appelhans & W.L. Wagner sp. nov. urn:lsid:ipni.org:names:60472944-2 Figs 1 , 4 , 5
Figure 1.

K.R. Wood, Appelhans & W.L. Wagner. A Flowering branch, Oppenheimer & Hansen H20505 (PTBG) B Inflorescence C Undehisced fruit, showing beaked carpels D Fruit, partly open E Fruit, fully opened F Fruit endocarp showing venation and hairs B–F from Oppenheimer & Miller H90609 (PTBG) (Illustration by Alice Tangerini).

Figure 4.

Habit of (Oppenheimer & Miller H90609). Photo by H. Oppenheimer, 12 Sep 2006.

Figure 5.

A Flowers B Fruit, showing beaked carpels (Oppenheimer & Miller H90609). Photos by H. Oppenheimer, 12 Sep 2006.

Diagnosis.

Differs from Hawaiian congeners by its combination of leaves having 7–10 pair of secondary veins; cymes to 3 cm long; peduncles 5–6.5 mm long; flowers perfect; carpels basally connate 1/5, narrowed into a strongly reflexed beak 10–15 mm long, capsules 4–9 × 40–52 mm; and ovary appressed densely short-sericeous.

Type.

United States of America. Hawaiian Islands, West Maui: Wailuku District, Waihe‘e Valley, - wet forest, , 770 m elev., 12 Sep 2006, Hank Oppenheimer & Jill Miller H90609 (holotype: PTBG-070667; isotypes: BISH, US)

Description.

3–4 m tall, bark medium brown, young branchlets light brown, glabrate, 3–6 mm wide in third internode, terminal branchlets yellowish brown tomentose with a waxy scurf. opposite, unifoliolate, coriaceous, the blade obovate to broadly elliptic, occasionally orbicular, 5–17.5 × 3.5–8.5 cm, the margin entire, the base rounded to obtuse, the apex rounded, obtuse to acute, or emarginate, secondary veins usually 7–10 pairs, connected by a moderately arched vein 2–11 mm from margin with higher order venation reticulate, both surfaces glabrous, occasionally glabrate along midrib of abaxial surface, young leaves glabrate to sparsely puberulent on lower surface; petiole shallowly canaliculate, 10–30 × 1–3 mm at middle, glabrate. : perfect, 3–5 in axillary cymes up to 3 cm long, peduncles 5–6.5 mm long, sparsely short-puberulent, pedicles 5–8 mm, short-puberulent, bracteoles 1.5–3 mm long, sepals broadly ovate, tip short acuminate, externally sparsely short-puberulent, glabrous within, 3 × 2.5–2.8 mm, connate basally 1/4 to 1/3 of length; petals tinged purple, narrowly ovate, lanceolate, 6–8 × 2.5–3 mm, glabrous internally and externally, tips recurved, nectary disk with sparsely scattered hairs; ovary densely appressed short-sericeous; style ca. 1.7 mm long, with finely appressed hairs; stigma capitate, four lobed, glabrous; stamens 8, filaments glabrous, the antesepalous ones 5–7 mm long, antepetalous ones 4–5 mm long, all with pollen. purple tinged when fresh, 4–9 × 40–52 mm, carpels connate basally for ca. 1/5 their length, narrowed into a strongly reflexed beak 10–15 mm long, exocarp glabrate with few hairs widely spaced over surface, endocarp sparsely to evenly puberulent. 2 per carpel, ovoid, 5–9 mm long.

Phenology.

To date, has been observed with flower buds in January and August, with flowers at anthesis during September, and with fruit during January, February, May, August, September, and November.

Etymology.

We are pleased to name this new species in honor of Hank Oppenheimer, botanist with the Maui Nui Plant Extinction Prevention Program, who collected the type specimen and has made many valuable contributions to the understanding and conservation of the Hawaiian flora.

Specimens examined.

United States. Hawaiian Islands, West Maui: Wailuku District, Waihe‘e Valley, south side, below and north of Kahoolewa Ridge, , 770 m elev., 8 Aug 1998, Wood & Perlman 7408 (BISH, PTBG, US); loc. cit., 9 Aug 1998, Perlman & Wood 16,338 (CANB, PTBG); loc. cit., 10 AUG 1998, Wood & Perlman 7419 (BISH, PTBG, US); loc. cit., 15 Feb 2005, Oppenheimer & Hansen H20,505 (BISH, PTBG, US); loc. cit., 19 May 2009, Perlman & Oppenheimer 21,642 (PTBG). The following couplets can be inserted into the existing key to Hawaiian (treated as ) by Stone, Wagner, and Herbst (in Wagner et al. 1999, pp. 1179–1182) to accommodate .

Distribution and ecology.

Although seven trees of have been documented since its discovery in 1998, only three trees are still surviving in the upper headwaters of Waihe‘e Valley, West Maui (Figures 2, 3). No trees have yet been located outside of the type locality and access to the site has only been by helicopter.
Figure 2.

Map of Maui, Hawai‘i showing location of in upper Waihe‘e Valley.

Figure 3.

Map of upper Waihe‘e Valley, West Maui, with red dot indicating the location of on the cliff-base plateau region.

K.R. Wood, Appelhans & W.L. Wagner. A Flowering branch, Oppenheimer & Hansen H20505 (PTBG) B Inflorescence C Undehisced fruit, showing beaked carpels D Fruit, partly open E Fruit, fully opened F Fruit endocarp showing venation and hairs B–F from Oppenheimer & Miller H90609 (PTBG) (Illustration by Alice Tangerini). Map of Maui, Hawai‘i showing location of in upper Waihe‘e Valley. Map of upper Waihe‘e Valley, West Maui, with red dot indicating the location of on the cliff-base plateau region. Habit of (Oppenheimer & Miller H90609). Photo by H. Oppenheimer, 12 Sep 2006. The plant communities of upper Waihe‘e Valley are varied and merge together in and around the 0.25 km2 cliff-base plateau region where trees of occur. The plateau itself represents a relictual low statured Banks ex Gaertn. ()- Nutt. ex Seem. () lowland wet forest community. Other relic native components of the plateau include ferns such as Mett. (), (Sm.) Hook. & Arn. (), PageBreak (Brack.) Copel. (), (C. Presl) Diels (), two endemic genera of ferns, namely Gaudich. () and Kaulf. (), along with herbs, shrubs, and small trees including H. Mann (), Gaudich. (), A. Gray (), Gaudich. (), C. DC. (), and various species of Gaudich., Gaudich. (both ), and J.R. Forst. & G. Forst. (). Steeper ridges and slopes that edge the plateau are dominated by matting ferns of Bernh.() (Wood 1997). Unfortunately, past habitat degradation by introduced pigs ( L.) has altered the plant composition of the plateau, which is now being dominated by a succession of invasive weeds, which threaten , especially (Spreng.) R.M. King & H. Rob. (), Lour. (), (L.) D. Don (), DC. (), and (DC.) Cogn. () (Wood 1997). Towering over the plateau and most outstanding, are vertical caldera-like basalt cliffs dominated by a native sedge and grass association called Vahl ()- P. Beauv. () wet cliff community. The cliffs are seeping with springs and waterfalls and strata of past volcanic flows are clearly evident. Additional components of this Waihe‘e cliff community include PageBreakHook. & Arn., (Hook. & Arn.) A. Gray (), Hillebr., Munro ex Hillebr. (both ), and (DC.) D.D. Keck. Superb examples of - montane wet forest dominate above these cliffs in association with windswept wet shrublands and occasional bog communities in and around the locality known as Kaho‘olewa Ridge (Wood 1997). At the base of the cliffs, which enclose the southern perimeter of the plateau lie heaps of basalt talus with accumulated substrates which are moderately deep in sections and appear to be fine textured brown silty clay. The forests spreading below the plateau are composed of mixed lowland riparian vegetation, which are closed to open in canopy and dissected by deeply PageBreakcarved streams with steep banks 10–30 m in height. The native flora of this lower riparian community has similarities to the cliff-base plateau but with a greater diversity, including Hook. & Arn. (), A. Gray (), (A. Gray) Lowry & G.M. Plunkett (), and Rock (), along with species of Cham. & Schltdl. (), L. (), and L. () (Wood 1997). Notable observations of native birds in the upper Waihe‘e region include nesting seabird colonies of dark-rumped petrels ( Ridgeway) along with native forest birds such as ‘apapane ( Gmelin), and ‘amakihi ( Rothschild).

Phylogenetic placement.

, like all Hawaiian , falls into , which has a distribution ranging from Taiwan, the Philippines, and Borneo eastward to the Hawaiian and Marquesas Islands, and south to New Caledonia. Only (Lam.) Merr. is distributed in the Southeast Asian areas mentioned above, and the remainder of is restricted to New Guinea and PaPageBreakcific archipelagos (Hartley 2001). proved to be polyphyletic in molecular phylogenetic analyses, and monophyly can be reached if the New Caledonian species are excluded and the Hawaiian endemic genus is included in the section (Appelhans et al. 2014b). Hartley (2001, pp. 31, 139–140) stated that the Hawaiian species mostly resemble the New Caledonian species – especially – based on several “primitive” characters including bisexual flowers, persistent sepals and petals, apically acute staminal filaments, basally connate carpels, glabrous endocarp, and Type A seed attachment, however, a close phylogenetic relationship of the Hawaiian and the New Caledonian species could not be verified (Appelhans et al. 2014b). The Hawaiian species of have been treated under the genus by Wagner et al. (1990) and the authors divided the taxon into the four sections B. Stone; B. Stone; B. Stone; and . If the Hawaiian groups are to continue to be recognized, they would need to be treated as subsections. Only the latter of these sections, which consists of three species, proved to be monophyletic (Appelhans et al. 2014b, c). Two specimens of (the paratypes Wood & Perlman 7408 and Wood & Perlman 7419) have been included in phylogenetic research (Appelhans et al. 2014b, c) and they are listed under the original determination (H. St. John) T.G. Hartley & B.C. Stone in these studies. The two specimens are part of a largely unresolved clade consisting of representatives of and . The closest relatives of could not be determined due to the low genetic variation in the sampled nuclear and plastid markers. We are currently working on resolving phylogenetic relationships of Hawaiian using Next-generation sequencing.

Morphology and related taxa.

Although beaked fruit have evolved in a few species of belonging to sections and (Hartley 2001, p. 19), this character is unique to within (Figure 1C, 5B). Beaked fruit have also evolved in Hawaiian B.C. Stone, which is nested within , but which is not an immediate relative of . A Flowers B Fruit, showing beaked carpels (Oppenheimer & Miller H90609). Photos by H. Oppenheimer, 12 Sep 2006. Morphologically, resembles the Moloka‘i endemic species , with both having reflexed carpels that are coherent at base. Significant differences between and include capsules connate 1/5, 4–9 × 40–52 mm (vs. capsules connate 1/4, 10–17 × 20–33 mm); endocarp sparsely to evenly puberulent (vs. endocarp glabrous); ovary appressed densely short-sericeous (vs. ovary glabrous); pedicles 5–8 mm (vs. pedicles15–20 mm); and flowers perfect, 3–5, on robust peduncles (vs. flowers unisexual, 1–3, on delicate peduncles). Two other morphologically similar Hawaiian , also with carpels coherent at base include (Hillebr.) T.G. Hartley & B.C. Stone and (A. Gray) T.G. Hartley & B.C. Stone. , which is known from Molokai and Maui, differs from in having capsules connate 1/4, 10–17 × 21–39 mm; endocarp glabrous; ovary glabrous; and flowers unisexual. , which is known from Lana‘i, Moloka‘i, East Maui, and the big island of Hawai‘i, similarly differs with capsules connate 1/3–1/4, and flowers unisexual, yet PageBreakalso differs with leaves having 10–20 pair of secondary veins; cymes ca. 6 cm long; and peduncles 7–38 mm long. has leaves with 7–10 pair of secondary veins; cymes ca. 3 cm long; and peduncles 5–6.5 mm long. species are generally either exclusively hermaphroditic or dioecious, yet there are a few recorded exceptions (Hartley 2001, p. 10). Although is apparently hermaphroditic, we cannot make a definitive statement on the breeding system of this rare narrow endemic, having only six collections for study, and limited flowering material.

Conservation status.

Plant and animal endemics from isolated oceanic islands are often endangered or critically endangered (Kreft et al. 2008, Sakai et al. 2002). The ongoing decline of native pollinators (Kearns et al. 1998) and seed dispersers (Milberg and Tyrberg 1993), in combination with other primary extrinsic factors such as invasive non-native plants, predation by introduced vertebrates, loss and fragmentation of natural habitats, and devastation by severe storms, are leading to an increase in extinctions throughout the islands of Oceania (Sakai et al. 2002, Wood 2007, 2012, Kingsford et al. 2009). Other prominent factors such as strict habitat requirements, very low historic population densities and narrow geographic range increase the risk of extinction. (Sakai et al. 2002, Wood 2007, 2015). It is currently unclear how many of the estimated 10,000 native Hawaiian insect species have gone extinct, but at this point in time the Hawaiian Islands have lost 79 of its native bird species and are left with only 32 (James and Olson 1991, Olson and James 1991, Burney et al. 2001, Boyer 2008). The authors maintain a checklist of endemic Hawaiian vascular plant taxa that have no known wild individuals remaining. Of the estimated 1191 native vascular plant species in Hawai‘i, 130 taxa are now presumed extinct. Evidently 41 of these possible extinctions have occurred in the Hawaiian lobeliads (), a family renowned for their co-evolution with Hawai‘i’s unique forest birds, the honeycreepers, in the endemic subfamily of the or finch family (Wood 2014, 2015). The or mint family falls second in this severe category, with 22 species that are presumed extinct. With two-thirds of the surviving forest bird species in Hawai‘i being critically PageBreakPageBreakendangered and a continued decline in native arthropods, there is grave concern for the endangered Hawaiian flora and for their unique insular relationships with biodiversity as a whole. Even today, little is known about the life cycles, breeding system variations, and habitat preferences found in the Hawaiian flora (Sakai et al. 2002, Wood 2015), but it is known that rely on insects for pollination and birds for dispersal (Hartley 2001). Within Hawaiian five species are currently presumed extinct, 19 are federally listed as endangered, and with the inclusion of , ten species fall into the category, meaning there are 50 or fewer individuals remaining (see Table 1). Members of Hawaiian are currently in the process of being evaluated according to IUCN categories and criteria.
Table 1.

Checklist of endemic Hawaiian and with conservation status and island distribution. (Status Symbols: C=candidate for federal listing; E=federally listed as endangered; EX; PEPP=Plant Extinction Prevention Program (50 or less individuals known in wild); SOC. Island Distribution: K=Kaua‘i; O=O‘ahu; Mo=Moloka‘i; L=Lana‘i; M=Maui; H=Big Island of Hawai‘i; Note: had been shown to be nested in [Harbaugh et al. 2009, Appelhans et al. 2014c]).

=possibly extinct

=species of concern

TaxonStatusDistribution
Melicope adscendens (H.St.John & E.P.Hume) T.G.Hartley & B.C.StoneE, PEPPM
Melicope anisata (H.Mann) T.G.Hartley & B.C.StoneK
Melicope balloui (Rock) T.G.Hartley & B.C.StoneE, EXM
Melicope barbigera A.GrayK
Melicope christophersenii (H.St.John) T.G.Hartley & B.C.StoneEO
Melicope cinerea A.Gray SOC O
Melicope clusiifolia (A.Gray) T.G.Hartley & B.C.StoneK, O, Mo, L, M, H
Melicope cruciata (A.Heller) T.G.Hartley & B.C.Stone SOC K
Melicope degeneri (B.C.Stone) T.G.Hartley & B.C.StoneE, PEPPK
Melicope elliptica (A.Gray) T.G.Hartley & B.C.StoneO, Mo, M
Melicope feddei (H.Lév.) T.G.Hartley & B.C.StoneK
Melicope haleakalae (B.C.Stone) T.G.Hartley & B.C.Stone SOC M
Melicope haupuensis (H.St.John) T.G.Hartley & B.C.StoneE, PEPPK
Melicope hawaiensis (Wawra) T.G.Hartley & B.C.Stone SOC Mo, L, M, H
Melicope hiiakae (B.C.Stone) T.G.Hartley & B.C.StoneEO
Melicope hosakae (H.St.John) W.L.Wagner & R.K.ShannonO
Melicope kaalaensis (H.St.John) T.G.Hartley & B.C.StoneO
Melicope kavaiensis (H.Mann) T.G.Hartley & B.C.StoneK
Melicope knudsenii (Hillebr.) T.G.Hartley & B.C.StoneE, PEPPK, M
Melicope lydgatei (Hillebr.) T.G.Hartley & B.C.StoneE, PEPPO
Melicope macropus (Hillebr.) T.G.Hartley & B.C.StoneEX, SOCK
Melicope makahae (B.C.Stone) T.G.Hartley & B.C.StoneEO
Melicope molokaiensis (Hillebr.) T.G.Hartley & B.C.StoneMo, M
Melicope mucronulata (H.St.John) T.G.Hartley & B.C.StoneE, PEPPMo, M
Melicope munroi (H.St.John) T.G.Hartley & B.C.StoneEMo, L
Melicope nealae (B.C.Stone) T.G.Hartley & B.C.StoneEX, SOCK
Melicope oahuensis (H.Lév.) T.G.Hartley & B.C.StoneO
Melicope obovata (H.St.John) T.G.Hartley & B.C.StoneEX, SOCM
Melicope oppenheimeri K.R.Wood, Appelhans & W.L.Wagner PEPP M
Melicope orbicularis (Hillebr.) T.G.Hartley & B.C.StoneM
Melicope ovalis (H.St.John) T.G.Hartley & B.C.StoneEM
Melicope ovata (H.St.John & E.P.Hume) T.G.Hartley & B.C.StoneK, O
Melicope pallida (Hillebr.) T.G.Hartley & B.C.StoneEK, O
Melicope paniculata (H.St.John) T.G.Hartley & B.C.StoneEK
Melicope peduncularis (H.Lév.) T.G.Hartley & B.C.StoneK, O, Mo, M
Melicope pseudoanisata (Rock) T.G.Hartley & B.C.StoneM, H
Melicope puberula (H.St.John) T.G.Hartley & B.C.StoneEK
Melicope quadrangularis (H.St.John & E.P.Hume) T.G.Hartley & B.C.StoneE, PEPPK
Melicope radiata (H.St.John) T.G.Hartley & B.C.StoneH
Melicope reflexa (H.St.John) T.G.Hartley & B.C.StoneE, PEPPMo
Melicope rotundifolia (A.Gray) T.G.Hartley & B.C.StoneO
Melicope saint-johnii (E.P.Hume) T.G.Hartley & B.C.StoneEO
Melicope sandwicensis (Hook. & Arn.) T.G.Hartley & B.C.Stone SOC O
Melicope sessilis (H.Lév.) T.G.Hartley & B.C.StoneMo, M
Melicope volcanica (A.Gray) T.G.Hartley & B.C.StoneMo, L, M, H
Melicope waialealae (Wawra) T.G.Hartley & B.C.StoneK
Melicope wailauensis (H.St.John) T.G.Hartley & B.C.StoneEX, SOCMo
Melicope wawraeana (Rock) T.G.Hartley & B.C.StoneK, O
Melicope zahlbruckneri (Rock) T.G.Hartley & B.C.StoneE, PEPPH
Platydesma cornuta Hillebr. var. cornutaEO
Platydesma cornuta Hillebr. var. decurrens B.C.StoneEO
Platydesma remyi (Sherff) O.Deg., I.Deg, Sherff & B.C.StoneC, PEPPH
Platydesma rostrata Hillebr.EK
Platydesma spathulata (A.Gray) B.C.StoneK, O, M, H
Plant Extinction Prevention Program Checklist of endemic Hawaiian and with conservation status and island distribution. (Status Symbols: C=candidate for federal listing; E=federally listed as endangered; EX; PEPP=Plant Extinction Prevention Program (50 or less individuals known in wild); SOC. Island Distribution: K=Kaua‘i; O=O‘ahu; Mo=Moloka‘i; L=Lana‘i; M=Maui; H=Big Island of Hawai‘i; Note: had been shown to be nested in [Harbaugh et al. 2009, Appelhans et al. 2014c]). =possibly extinct =species of concern IUCN Red List Category. When evaluated using the World Conservation Union (IUCN) criteria for endangerment (IUCN 2001), falls into the category, which designates this species as facing a very high risk of extinction in the wild. Our formal evaluation can be summarized by the following IUCN hierarchical alphanumeric numbering system of criteria and subcriteria: CR B1ab(i,ii,iii,v)+2ab(i,ii,iii,v); C2a(ii); D; which reflects a severely limited and of less than 1 km2 and a wild population of only three individuals. It should be noted that seed collections of have been made by Maui PEPP staff during routine monitoring and there is currently a single cultivated individual being grown at the Olinda Rare Plant Facility on East Maui. Critically Endangered Extent of Occurrence Area of Occupancy
19(18)Exocarp sparsely to densely puberulent or tomentose, at least toward base or along suture20
19Exocarp glabrous or glabrate, sometimes with a few hairs widely spaced over surface (49).49
49(19)Endocarp densely and uniformly short-villous; K Melicope cruciata
49Endocarp glabrous or sparsely puberulent, especially along suture50
50(49)Leaves ternate; O Melicope lydgatei
50Leaves opposite.51
51(50)Most petioles 0–10 mm long52
51Most petioles over 10 mm long58
58(51)Ovary sparsely to densely puberulent or tomentulose, but exocarp glabrate or nearly so in fruit59
58Ovary and exocarp glabrous60
59(58)Flowers perfect, carpels narrowed into a reflexed beak 10–15 mm long; WM Melicope oppenheimeri
59Flowers unisexual, carpels straight or somewhat reflexed, apex not beaked59a
59a(59)Capsules (16–)25–40(–50) mm wide, carpels connate 1/4–1/3 their length; pedicels 5–20 mm long; L, EM, H Melicope volcanica
59aCapsules 11–20 mm wide, carpels connate (1/3–)1/2 their length or more; pedicels 2–5 mm long; K, O Melicope wawraeana
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Journal:  Molecules       Date:  2021-01-28       Impact factor: 4.411

  4 in total

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